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Page 1: LHWP Information Sheets
Page 2: LHWP Information Sheets

Water efficiency and conservation ensure that we are making smart use of the water that we have. All members of

the lower Hunter community, including businesses, residents and Hunter Water, can take an active role in reducing

demands on the water supply by adopting water efficiency measures and reducing water leakage.

Residential water efficiency - Currently, the Hunter region has a high uptake of water efficient programs and

devices. The promotion and adoption of water saving appliances plays a key role in helping to increase these savings

every year. Two well-known examples of residential water efficiency initiatives are the showerhead exchange

program and the toilet replacement program.

Business water efficiency - Non-residential customers can have a strong influence on water efficiency by making

changes either in the way they use water, or by replacing drinking quality water with another source that is ‘fit-for-

purpose’. Actions may include retrofits to equipment, audits of water use, or installing data loggers to monitor and

better manage water use.

Loss minimisation - The pipes and infrastructure that make up the water supply network are subject to leaks, breaks

and overflows. Leaks occurring within the home can be identified and addressed by homeowners. Leaks in the

greater part of the network are addressed by Hunter Water.

Savings from water efficiency and loss

minimisation programs have increased

steadily in recent years, as shown in the

graph. In 2011-12, around 950 ML (1 ML

= 1 million litres) of drinking water was

saved from water efficiency measures,

and around 570 ML was saved from loss

minimisation measures.

This series of information sheets

outlines opportunities to build on water

efficiency and loss minimisation

programs.

To maximise the benefit of these

programs in the lower Hunter, it will be

important to consider the combination of measures

that achieve water savings while weighing up the

economic, social and environmental implications.

Water Efficiency

Water Efficiency - Overview

INFORMATION SHEET 1.0

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

0

500

1000

1500

2000

2006-07 2007-08 2008-09 2009-10 2010-11 2011-12

Vo

lum

e o

f W

ate

r (M

L)

Year

Drinking Water Savings

Water efficiency Loss minimisation

Page 3: LHWP Information Sheets

What is non-residential water efficiency?

Water efficiency means making the most of the current sources of water and involves using less water and reducing

the wastage of water. Using water more efficiently can have both financial and environmental benefits for

customers and the broader community.

Non-residential customers include industries, small businesses, office buildings, schools, hospitals, shopping centres,

hotels, restaurants and recreational facilities. These customers can improve their water efficiency by:

using products that are more water efficient

changing the way they use water

minimising losses or wastage

using recycled water or treated stormwater in business or industrial processes instead of using drinking

quality water.

Other ways of improving non-residential water efficiency include:

audits of water use to identify opportunities to reduce water use. These audits can include looking at water

use in kitchens, cooling towers, amenities, steam generation, irrigation, etc

subsidies or incentives to install more water-efficient appliances (such as dual-flush toilets, water-saving

showerheads, washing machines and trigger-operated spray guns)

installing data loggers to continuously monitor water use and identify potential leaks

raising customer awareness by providing information and examples of how to save water.

What support is available for non-residential customers?

Hunter Water currently has four programs to help non-residential customers improve their water efficiency. These

are outlined in the table below, along with an indication of the water savings that might be achieved.

The greatest water savings generally involve the largest water users. Hunter Water has about 30 ‘water-intensive’

customers who each use more than 50 ML (1 ML = 1 million litres) each year. Together they make up over 50% of

non-residential usage, so programs that focus on these customers are likely to produce the largest water savings.

Program Target Market Potential Water Savings

Large customer audit program Major customers (use more than 50ML/year) 10-25% for each participant for all

uses

Hunter Business Water

Savers Program

Commercial customers who use significant quantities of water in

their bathrooms and kitchens for non-drinking water purposes

30% of total bathroom and kitchen

uses

Irrigation water efficiency

audits

All irrigation activities such as public open spaces, sports fields

and school ovals

30% of total irrigation uses

Hunter Water facilities audit Wastewater treatment plants 15% average for each site, based on

site assessments completed so far

Water Efficiency

Non-Residential Water Efficiency

INFORMATION SHEET 1.1

Page 4: LHWP Information Sheets

While the existing programs focus on helping customers to use water more efficiently in ‘normal’ (non-drought)

times, a further step could target greater water efficiency during drought through voluntary or mandatory programs.

These might include:

increasing levels of customer contact and education

offering incentives for retrofitting water-efficient equipment

providing funding for customers to implement actions identified in water use audits

requiring large customers to develop and implement water efficiency management plans.

Some of these concepts are also explored in Information Sheet 2.2 on Drought Restrictions.

What do other water authorities in Australia do?

Most water authorities in Australia have supported a range of non-residential water efficiency initiatives over a

number of years. The most common initiatives are audits of major customers to develop water efficiency

management plans and monitoring programs to detect leaks.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Customer participation rates may be low in voluntary programs,

particularly for customers where water is a relatively small cost

Follow up is needed to make sure that water saving initiatives

identified in water use audits have been implemented

Community support is vital for water efficiency programs

Effective incentives and enforcement of mandatory programs may be

needed to achieve savings in a drought

Environmental considerations

Reducing demand for water may delay the need to implement other

major infrastructure measures

Social considerations

Encourages water efficient behaviour

Demonstrates that saving water is a shared responsibility between

businesses and the community

Some business customers may find it difficult to absorb the cost of

equipment upgrades and/or retrofits

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 5: LHWP Information Sheets

What does residential water efficiency mean?

Members of the community can influence how water-

efficient they are simply by changing some of the ways

they use water and by choosing water efficient appliances

for the home.

Examples of residential water efficiency include installing

water efficient showerheads, tap aerators and dual flush

toilets, using trigger nozzles for garden hoses, and

choosing garden plants that need less water.

Water efficiency can also be improved by buying more

water-efficient washing machines and dishwashers when

they need to be replaced.

What water efficiency programs are available in the Hunter region?

Hunter Water has recently reviewed the effectiveness of its water efficiency incentive programs. This review found

that households that took part in the toilet replacement program (replacing single-flush toilets) saved an average of

20 kilolitres of water a year. Those households that took part in the showerhead exchange program saved an

average of 12 kilolitres of water a year.

Existing water efficiency initiatives could be expanded to achieve greater savings. Initiatives such as incentives to

purchase and install water efficient washing machines and toilets, making comparative water use information

available on customer bills, and education and behavioural change programs are some potential ways of saving more

water.

Some initiatives may achieve higher water savings, for example smart metering and advanced water bills that

compare water use details based on occupancy. However, given the relatively high level of residential water

efficiency in the lower Hunter, the cost to implement these initiatives can be significant compared to the amount of

water saved.

What is happening in other parts of Australia?

Many areas throughout Australia have put in place a range of residential water efficiency initiatives directed at both

managing demand in normal times, and reducing water use in drought.

The BASIX program applies to new homes that are built in New South Wales. BASIX is a planning policy that makes

sure new residential properties are designed to use less drinking water, for example by installing a 4-Star WELS

shower head or installing a rainwater tank (see Information Sheet 3.2 for more information). BASIX also applies to

major renovations in existing homes.

Water Efficiency

Residential Water Efficiency

INFORMATION SHEET 1.2

Installing a water efficient showerhead is an

inexpensive way to improve water efficiency in the home

Page 6: LHWP Information Sheets

At a national level, the Water Efficiency Labelling and Standards (WELS) scheme requires certain appliances and

products to be registered and labelled with their water efficiency rating. This helps Australian consumers choose

products that save water and reduce their water and energy bills. The scheme began in 2005 and covers showers,

taps, toilets, urinals, washing machines and dishwashers.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Water savings may tend to taper off once the uptake of a particular

water saving device (such as showerheads and dual flush toilets) has

neared saturation, unless there are further innovations in

technology

Environmental considerations

Encourages the use of drought tolerant plants

Reducing demand for water may delay the need to implement other

major infrastructure measures

Social considerations

Can reduce individual household water bills

Encourages investment in innovation and alternative water

efficiency technology

Can reduce individual household water bills due to more efficient

hot water usage

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 7: LHWP Information Sheets

What is water loss minimisation?

Water supply systems around the world all lose some water due to leaks and watermain breaks. Most water utilities

have programs to reduce water losses from their systems in a cost-effective manner.

How can water loss be minimised?

Programs to reduce losses include active leak detection and water pressure management programs which are

discussed below. Other activities that help to reduce losses include replacing sections of water mains that have a

history of breaks, replacing leaking water services (that is, the pipes between the water main and the meter), and

responding more quickly to breaks or leaks in the water supply system.

Hunter Water estimates that leakage from the system has reduced by 30% over the last eight years.

What is water loss benchmarking?

Water utilities like Hunter Water benchmark their water loss performance using an international system called the

Infrastructure Leakage Index (ILI). The ILI shows how current actual losses (leakage) compare with the theoretical

lowest possible level of leakage that could be achieved by an agency’s water supply system. Hunter Water’s ILI is

ranked in the ‘excellent’ category, along with most major Australian water utilities.

What is active leak detection?

Leaks occur in all water supply systems particularly as the pipes age. Active leak detection is the use of listening

devices to survey water supply networks and identify leaks before they would normally be seen and reported.

This helps detect some leaks that may not be visible and might never be reported, such as leaks that drain below the

ground to the stormwater system or waterways.

The 2011-12 active leak detection program covered 1160 kilometres of water mains across the west Lake Macquarie

and Coalfields districts. The survey found 163 leaks corresponding to estimated water loss savings of 214 ML.

Currently active leak detection occurs across the

Hunter Water system on a five-year program.

Water Efficiency

Water Loss Minimisation

INFORMATION SHEET 1.3

Repairing a water main

Page 8: LHWP Information Sheets

How does pressure management work?

Some customers receive water at very high pressure due to the set-up of the water distribution system and the local

terrain. For example, houses that are at the bottom of hills can receive high pressure water if the local water

reservoir is situated high in the landscape. This very high pressure can result in the pipes developing a leak.

Pressure management in these areas reduces the flow rate to customers. This reduces the frequency and volume of

leaks. Pressure is reduced by changing the way the network is configured or using a special valve.

Options for expanding Hunter Water’s active leak detection and pressure management programs will be considered

as part of the development of the Lower Hunter Water Plan.

Schematic showing why homes receive water at different pressures

Page 9: LHWP Information Sheets

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

ACTIVE LEAK DETECTION LOW MEDIUM HIGH

Water

Cost

Lead time

PRESSURE MANAGEMENT LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

It can be technically difficult to establish pressure management

zones depending on the landscape and how the water network fits

together

There are few studies on the long term costs and benefits

Environmental considerations

Reducing water losses may delay the need to implement other

major infrastructure measures

Social considerations

Demonstrates that saving water is a shared responsibility between

Hunter Water and the community

Pressure management potentially extends asset life and reduces

customer inconvenience from water supply interruptions by

reducing the variations in operating pressure which can cause

infrastructure to fail (e.g. burst water mains)

Pressure management can be effective in reducing customer water

use due to lower flow rates and lower leakage within the home

Customers may be concerned by the difference in pressure

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 10: LHWP Information Sheets

Ensuring that a secure supply of water is available relies on balancing both supply and customer demand. With every

measure that reduces customer demand, more water remains in storage, possibly reducing the need for major

investment in new infrastructure on the supply side.

In Australia and internationally, a broad range of approaches are used to manage demand, including pricing and

restrictions.

The lower Hunter was the first region to introduce user pays water pricing in the early 1980s. This is now the

standard throughout Australia. As the Independent Pricing and Regulatory Tribunal (IPART) is responsible for the

pricing structure for water supplied by Hunter Water, these information sheets will not cover pricing as a demand

management measure.

Demand management activities can be permanent or temporary, voluntary or mandatory. Whichever approach is

taken, community support is critical. Demand management will be more successful where the community is engaged

in planning a demand management strategy and is committed to using water wisely.

This series of information sheets discusses three

potential demand management strategies for the

Lower Hunter Water Plan:

Water Wise Rules – simple, common sense

actions that help save water every day.

Drought restrictions – put in place during

times of drought to slow down the drop in

water storages.

Voluntary water use targets – sometimes

used during extreme drought to encourage

customers to voluntarily reduce water use

inside the home. These would be used in

addition to drought restrictions.

Demand

Management

Demand Management - Overview

INFORMATION SHEET 2.0

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

Use of a trigger nozzle helps reduce water wastage

Page 11: LHWP Information Sheets

What are Water Wise Rules?

Water Wise Rules are simple, common sense actions that help conserve water every day. They are sometimes

referred to as ‘permanent water conservation measures’.

Water Wise Rules already apply in the area serviced by Sydney Water (Sydney, the Blue Mountains and the

Illawarra), as well as on the Central Coast and many towns throughout NSW. The rules apply to residents,

businesses, local councils and government agencies. In some areas, including Sydney, fines can be applied for

breaches of the rules.

Water Wise Rules were introduced in Sydney in 2009 following the lifting of drought water restrictions which had

been in place for nearly six years. The Central Coast also introduced permanent Water Wise Rules in 2012, after a

decade of water restrictions.

The lower Hunter has not experienced a similar lengthy period of water restrictions since the 1980s, as it was

fortunate during the last drought that the water storages were replenished by significant rainfall in 2007.

The development of the Lower Hunter Water Plan provides a timely opportunity to seek community feedback on

whether this region should introduce Water Wise Rules and, if so, what these rules should be.

What is currently in place in the lower Hunter?

Although the lower Hunter does not have Water Wise Rules at present, Hunter Water does promote a range of

water-saving tips to help the community save water in the home and garden. These include using a trigger nozzle to

water plants and a broom rather than a hose for cleaning hard surfaces to reduce water wastage. Only using a

sprinkler before 10am and after 4pm, when the heat of the sun is no longer at its peak, to help to minimise natural

evaporation from lawns and gardens. Reducing your shower time and only using the washing machine and

dishwasher with full loads to improve household water use. More tips can be found at

www.hunterwater.com.au/Save-Water/Save-Water.aspx.

Demand

Management

Water Wise Rules

INFORMATION SHEET 2.1

The Water Wise Rules introduced for Sydney and the Central Coast are similar to each other and focus on

outdoor water use. If comparable rules were implemented in the lower Hunter, they could include:

Watering with a sprinkler, irrigation system or trigger nozzle hose, is permitted any day before 10am or

after 4pm to avoid the heat of the day

All hand held hoses must have a trigger nozzle

No hosing of hard surfaces such as paths and driveways

All vehicles should be washed with a bucket, trigger nozzle hose or pressure cleaner

Page 12: LHWP Information Sheets

Where are Water Wise Rules applied in Australia?

The ACT, South East Queensland, Adelaide, Sydney and the Central Coast all have various types of Water Wise Rules

in place. These rules were generally introduced at the time drought restrictions were lifted, when community

awareness of water saving behaviour was particularly high.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Community support is vital when introducing Water Wise Rules,

particularly if this occurs when restrictions have not been in place

for a long time.

Water Wise Rules could be either advisory or enforceable.

Enforceable rules could be implemented under the Hunter Water

Regulation 2010.

Given the relatively high level of residential water efficiency in the

lower Hunter, Water Wise Rules may not result in as much savings

as in some other jurisdictions

Environmental considerations

No new infrastructure required

Reducing demand for water may delay the need to implement

other major infrastructure measures

More efficient use of water in the garden by reducing evaporation

and waste

Encourages use of drought tolerant plants

Social considerations

Encourages water efficient behaviour both indoors and outdoors

Community actively contributes to water security

Consistency with most large cities in Australia and adjacent regional

areas

Can reduce individual household water bills

Some household activities may be inconvenienced

Potential for fines to apply for breaching the rules

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 13: LHWP Information Sheets

Why do we need drought restrictions?

Water use restrictions can be used to limit water use in and around the home and by non-residential customers.

Restrictions can be implemented in times of drought to help reduce the demand for water and slow down the drop

in water storages.

What types of restrictions are used?

Drought restrictions apply to all households equally. They may include actions such as banning fixed sprinklers,

limiting hours and days that hoses can be used, requiring hoses to have a trigger nozzle and banning outdoor use

completely when storage levels are very low.

Water use by non-residential customers is quite diverse, and reductions in water use may be achieved more

effectively through customised programs for similar groups of customers. Programs to improve non-residential

water efficiency (as discussed in Information Sheet 1.1) could be extended in drought times when restrictions apply.

For example, the development and implementation of water efficiency management plans could be made

mandatory for medium-large water users.

Restrictions are mandatory and enforceable under the Hunter Water Regulation 2010. Some exemptions may apply,

such as for public health reasons or for customers with special needs.

Different restrictions would be triggered when the total water storage volume reaches various levels. Current trigger

levels for the Hunter are:

1. low restriction (60% storage)

2. medium restriction (50% storage)

3. high restriction (40% storage)

4. extreme restriction (30% storage).

The figure below shows target usage levels and an indication of the type of restrictions that would be in place for

residential customers. As discussed above, non-residential water restrictions may be more complex due to the

diversity of water use.

Demand

Management

Drought Restrictions

INFORMATION SHEET 2.2

The targets are for use per

person in litres per day (LPD)

Page 14: LHWP Information Sheets

Other options include rules similar to Sydney (Water Wise Rules plus two levels of restrictions) or the Central Coast

(Water Wise Rules plus five levels of restrictions). Having similar drought restriction rules to neighbouring regions

could be beneficial as it may minimise confusion for people moving or travelling between regions.

What restrictions are used in other parts of Australia?

Many Australian cities have planned for and used drought restrictions. The majority of these have been staged, with

more severe water restrictions being implemented as storage levels drop.

Restrictions have applied to watering gardens and lawns, filling pools, cleaning vehicles and boats, washing hard

surfaces and pavements and using water on recreational fields and parks.

Residential water use restrictions were previously implemented by Hunter Water in droughts during the 1990s,

1980s and 1960s.

Restricting outdoor water use was a key element in securing Sydney’s water supply during the most recent drought,

with restrictions in place from 2003 until 2009. The restrictions on outdoor water use were progressively increased

in response to declining storage levels. Water Wise Rules were introduced when drought restrictions were lifted in

2009. Water Wise Rules are discussed in Information Sheet 2.1.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

From low to medium, depending on length of drought

Cost

Lead time

Implementation considerations

Community is familiar with the concept of restrictions although they

have not been applied in the lower Hunter for some time

It is important for communication with customers on restrictions to

be regular, clear and consistent.

Environmental considerations

No new water supply infrastructure required

Reducing demand for water may delay the need to implement other

major infrastructure measures

Encourages use of drought tolerant plants

Loss of plants and animal habitat in the urban environment due to

lack of water

Social considerations

Encourages water efficient behaviour both indoors and outdoors

Some household activities may be inconvenienced

Adverse impacts on gardens and playing fields

Reduces individual choices about water use

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 15: LHWP Information Sheets

What are voluntary water use targets?

Voluntary water use targets are a way of encouraging further community water conservation during drought. They

involve encouraging people to achieve a set target for maximum daily water use per person.

Water use targets are usually put in place when restrictions have reached the maximum level (including a total ban

on outdoor use) yet water storage levels are continuing to drop.

The target is a way of encouraging the community to make voluntary reductions in indoor water use to achieve more

savings – effectively rationing their water use. They are called ‘voluntary’ because indoor restrictions cannot be

enforced.

Voluntary water use targets are implemented using substantial multi-media campaigns. Monitoring is usually via

feedback to the community of the area’s water use per person in litres per day (LPD) using a range of media.

What might this look like in the lower Hunter?

The average water use for unrestricted residential demand in the lower Hunter is currently 198 LPD per person.

Depending on the drought conditions, the aim of voluntary water use targets would be to reduce the water use to a

target level in the order of, say, 140 LPD per person. The community would be asked to reduce indoor water use

with actions such as having shorter showers and minimising waste in the bathroom, kitchen and laundry.

The indicative target of 140 LPD per person (29% savings compared to average use) is based on water usage in the

home and outdoors in the lower Hunter as well as considering the experience of other water authorities in the last

drought.

Where are voluntary water use targets used in Australia?

Major metropolitan centres in Australia - such as Melbourne and South East Queensland - have introduced voluntary

water targets during drought. These were applied in addition to drought restrictions. During the recent drought in

south eastern Australia, Melbourne set a voluntary personal water use target of 155 LPD per person and averaged

149 LPD per person over 2009-10.

South East Queensland successfully achieved a voluntary water target of 140 LPD in the recent severe drought. In

fact, South East Queensland residents reduced daily water use from a pre-campaign average of 179 LPD to 126 LPD,

and retained those reductions for more than a year.

The Central Coast’s minimum use during the recent drought was 153 LPD per person, very close to their target of

150 LPD per person. Even though restrictions have been lifted, the Central Coast has retained an ‘aspirational’

voluntary daily water use target of 150 LPD per person to encourage ongoing efforts to achieve high levels of water

efficiency.

Recent drought restrictions in the Sydney metropolitan area applied only to outdoor water use. Analysis of the water

savings achieved has found that about half the total reduction in demand occurred indoors. This suggests people are

willing to restrict their water use beyond the measures imposed by drought restrictions.

Demand

Management

Voluntary Water Use Targets

INFORMATION SHEET 2.3

Page 16: LHWP Information Sheets

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Voluntary targets and results would need to be communicated

widely to the community with associated costs

Voluntary targets are not enforceable

Tracking and reporting against the water use target would be done

at an average level across the community, although households

could monitor their own meter readings if they chose to do so

Environmental considerations

No new infrastructure required

Reducing demand for water may delay the need to implement

other major infrastructure measures

Social considerations

Community working together to achieve water saving goals

Provides choice about how people make savings within their home

and contribute to water security

May cause concerns about equity because some people will

contribute to voluntary reductions more than others

Some household activities may be inconvenienced

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 17: LHWP Information Sheets

Australia is one of the driest continents on earth and has one of the most variable rainfall patterns. The recent

droughts along much of the east coast of Australia have highlighted the importance of saving water and looking at

innovative solutions that capture rain when it is available rather than letting it just ‘run down the drain’ and into

waterways.

This series of information sheets looks at:

Stormwater harvesting

Rainwater tanks

Stormwater harvesting is the collection, treatment, storage and use of stormwater runoff from urban areas. It is

different from rainwater harvesting in that it is collected from drains or creeks, rather than from roofs. Stormwater

capture can provide large quantities of non-drinking quality water that may be useful for sports grounds, parks and

gardens, agriculture and flushing toilets. Stormwater runoff must be collected, stored and treated before it can be

used.

Rainwater tanks have been a valuable source of drinking water to many households in rural areas of Australia, where

a town water supply may not be available. Rainwater tanks can also be installed in new or existing homes with a

town water supply and the water can be used in place of drinking water for a variety of non-drinking uses.

In July 2005, the NSW Department of Planning expanded the Building Sustainability Index (BASIX) scheme to the

whole of NSW. BASIX is a sustainable planning measure to reduce water and energy use in homes across NSW.

In the Hunter Region, new homes are required to achieve a mandatory 40% reduction in potable water use

compared to average pre-BASIX volumes. Rainwater tanks have proven to be a popular choice in addressing BASIX

requirements with over 95% of single dwelling applications statewide nominating a rainwater tank as part of the

proposed development.

Whether it is rainwater from the roof or stormwater from the

catchment, water harvesting can play an important role in

reducing reliance on water storages.

Stormwater

Capture

Stormwater Capture - Overview

INFORMATION SHEET 3.0

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

Residential use of a rainwater tank

Page 18: LHWP Information Sheets

Stormwater

Capture

Stormwater Harvesting and Use

What is stormwater harvesting and use?

Stormwater harvesting and use is the collection, treatment, storage and use of stormwater runoff from urban areas.

It is different from rainwater harvesting as the runoff is collected from drains or creeks, rather than from roofs.

Stormwater runoff must be collected, stored and treated before it can be used. Storages may be open - in the form

of a pond, weir or lake - or enclosed in a tank either above or below the ground.

Urban stormwater collects contaminants as it passes over roads and other surfaces, picking up chemicals and

pathogens from the surrounding environment. Stormwater needs to be treated to a quality that suits how the water

will be used (eg, disinfection), according to public health and environmental guidelines.

Opportunities for stormwater use in the lower Hunter include irrigation of golf courses, public parks, sporting

grounds and fields. Stormwater can also be used in industry including wash down, dust suppression and other

operational processes. Another application is to substitute stormwater for drinking water for residential uses such as

toilet flushing, washing laundry and irrigation within community scale development.

A preliminary study has investigated stormwater harvesting at 17 case study sites such as golf courses, sporting

fields, and some industrial sites with high water use, where stormwater might be substituted for drinking water.

Is stormwater used widely in Australia and overseas?

Stormwater schemes continue to be successfully implemented across Australia, irrigating sports fields, golf clubs and

open spaces. Some of the largest annual water savings have been achieved by Bexley Municipal Golf Course (66

INFORMATION SHEET 3.1

Schematic showing stormwater harvesting, treatment, storage and use

Page 19: LHWP Information Sheets

million litres), and Northbridge Golf Club (92 million litres) in Sydney. Taronga Zoo uses treated stormwater to wash

down exhibit enclosures, public toilet flushing and irrigation of 10 hectares of land, saving over 36 million litres of

drinking water annually.

Numerous stormwater schemes operate overseas, often involving local councils in partnership with private

developers to use stormwater to irrigate parks and other public areas.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Typically the most cost effective case studies use an existing

storage facility; the least cost effective case studies require more

collection and treatment infrastructure

Grants can make a stormwater use scheme more viable for

proponents

Could be delivered by different organisations e.g. local councils,

private developers

The level of treatment required will vary depending on the

stormwater quality and end use

Construction may disturb existing infrastructure in suburban areas

Environmental considerations

Reduces stormwater pollution loads released into waterways

May reduce benefits to waterway health as less stormwater is

available for flushing flows

Potential environmental impacts during and after construction

Social considerations

Demonstrates that improving water security is a shared

responsibility

Maintains or improves the look, usability and safety of parks,

playing fields and other open spaces without using drinking water

Potential aesthetic impacts from a small treatment plant located

near park or playing field

Potential for health risks if water is not used as intended, or from

cross-connection with the drinking water supply

Potential safety risks and need to restrict public access

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

Page 20: LHWP Information Sheets

Why install a rainwater tank?

The recent droughts along much of the east coast of Australia have highlighted the importance of saving water and

looking at alternative water supplies. This has resulted in the collection of rainfall from roof run-off in urban areas

becoming an established practice for non-drinking uses of water.

Several State Governments and local water authorities have offered cash rebates toward the purchase of rainwater

tanks provided they were ‘plumbed in’ for toilet flushing and laundry use. The use of rainwater for appropriate

internal purposes provides the greatest savings from the drinking water supply.

While recognising that a properly maintained rainwater tank can provide good quality drinking water, NSW Health

states that in urban areas, ‘the public water supply remains the most reliable source of drinking water for the

community’, and supports the use of rainwater tanks in these areas ‘for non-drinking uses such as toilet flushing,

washing clothes or in water heating systems, and outdoors for uses such as garden watering, car washing, filling

swimming pools, spas and ornamental ponds, and firefighting.’ (Source: ‘Rainwater Tanks Brochure’, NSW Health,

2007).

Typically, rainwater tank systems involve a catchment area (roof) that collects and diverts rainwater to a storage

tank, prior to its use either in the garden or indoors. The system is usually backed up by the public mains water

supply to ensure the household water supply is not interrupted should rainwater storages run out.

Investigations into the role of rainwater tanks as an option for the Lower Hunter Water Plan are focused on:

understanding how many rainwater tanks are already installed

looking at how many new rainwater tanks could be installed

estimating potential water savings from rainwater tanks under both drought and average climatic conditions.

Are rainwater tanks used widely in Australia and overseas?

Information from the 2010 Census indicates that 32% of Australian households have a rainwater tank installed,

which is up from 24% in 2007 (ABS, 2010).

The use of rainwater tanks as a water conservation measure is internationally recognised, due to relatively low setup

costs, flexibility of design, and minimal maintenance requirements.

Stormwater

Capture

Rainwater Tanks

Toilet & Laundry

Roof run-off

Rainwater

Tank

Fixed speed

pump Mains water

switch valve

Outdoor use

INFORMATION SHEET 3.2

Typical configuration of a

rainwater tank system

integrated with the mains

(drinking) water supply

Page 21: LHWP Information Sheets

Examples of large scale rainwater use projects include the Fukoka Dome in Japan, which has a 35,000m2 catchment

area and collects rainwater to service 65% of low water quality demand including toilet flushing and irrigation. In

London, the Millennium Dome meets 10% of all onsite water demands even with storage constraints limiting

rainwater collection to a maximum 100 kilolitres/day.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Easily integrated in new developments but can also be retrofitted

to existing houses

Ongoing benefits rely on the system being properly maintained by

the property owner

Modifications to the system at a later date (e.g. leaf guards, first

flush diverters, plumbing) may reduce the efficiency or

performance of system

During dry times, tanks may be ‘topped up’ with drinking water

Environmental considerations

Collects water quickly during rain

Negligible environmental impacts as no major construction involved

Reduces stormwater pollution loads released into waterways

May reduce benefits to waterway health as less stormwater is

available for flushing flows

Cumulative energy use from widespread use of small pumps

Social considerations

Helps raise awareness of water conservation measures

Active community involvement in water management

Potential health risks if system is not properly maintained

Requires household behavioural changes and maintenance regime

Can increase household energy bills associated with water pumping

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

Page 22: LHWP Information Sheets

Water recycling is treating and reusing wastewater and greywater in homes, industry, irrigation and agriculture.

Stormwater harvesting and rainwater tanks are discussed in Information Sheets 3.0 - 3.2.

While recycled water can be used for a range of purposes, it must first be treated to a level that is considered ‘fit-for-

purpose’ - that is, it must be treated to a level appropriate for how it is going to be used. Generally speaking more

treatment will be required to produce higher quality water.

Water recycling in New South Wales includes widespread irrigation, large individual industrial water-users, and large

new residential developments in Sydney. Recycled wastewater is currently used in the lower Hunter for industry,

irrigation and agriculture.

Around 4,000 to 5,000 ML (1 ML = 1 million litres) of recycled water is typically used in the lower Hunter each year.

The planned Kooragang Industrial Water Scheme will increase the recycling rate by a further 3,300 ML by 2014. (For

further details on this project see Information Sheet 4.4.)

Examples of existing uses of recycled water in the lower Hunter include:

Industry - Eraring Power Station and the Oceanic Coal washery

Irrigation - local golf courses, a local trotting track and Kurri TAFE

Agriculture - a number of farms and the Karuah effluent reuse scheme.

The Recycled Water series of fact sheets describes a range of possible

options to increase the use of recycled water in the lower Hunter for non-

drinking water purposes, rather than using high quality drinking water for

such uses. These options include:

dual reticulation schemes – supplying recycled water through a

separate pipe network for purposes such as garden watering

and toilet flushing

greywater reuse – using household wastewater

(excluding toilets) for irrigation and other non-drinking

purposes

decentralised recycling schemes and sewer mining –

involving localised recycling schemes

industrial recycling – potential expansion of industrial

reuse.

Recycled Water

Recycled Water - Overview

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop,

go to haveyoursay.nsw.gov.au/lowerhunterwaterplan

INFORMATION SHEET 4.0

The National Water Commission has described some of the issues related to recycling wastewater as follows:

“The volume and percentage of recycled water are affected by a number of factors, including the availability of potable

water, the size of the utility, its proximity to potential customers (such as irrigators, major industrial customers and

recreational facilities) and government policy. Smaller regional centres often recycle a greater proportion of effluent than

larger metropolitan areas because discharge to inland rivers and streams often requires higher treatment, making recycling

more cost-effective; because regional towns often have greater access to willing buyers, such as agricultural businesses; and

because there are fewer alternative water supply options inland than on the coast”.

Purple pipes and taps indicate

recycled water

Options involving recycling for drinking water are not

being considered for the Lower Hunter Water Plan.

Page 23: LHWP Information Sheets

What is dual reticulation?

Dual reticulation means having two sets of pipes - one for drinking water and one for recycled water. Recycled

water pipelines can be built at the same time as drinking water mains in new suburbs. This is sometimes referred to

as a ‘third pipe’ system – that is, a pipe each for drinking water, sewer and recycled water.

Dual reticulation in new developments provides an opportunity for recycled water to be used for non-drinking water

purposes and contribute to meeting water use targets such as BASIX. Recycled water can be supplied for uses where

drinking water quality is not required, such as for flushing toilets, outdoor watering and industrial applications.

What has been investigated for the lower Hunter?

In the lower Hunter, water recycling opportunities have been investigated from each of the 19 wastewater

treatment plants operated by Hunter Water. The studies have considered opportunities to provide recycled water

to service larger new residential developments with highly treated fit-for-purpose recycled water to meet non-

drinking water quality demands. The success of such schemes depends on many factors including:

level of support from stakeholders

the distance between houses and the recycled water treatment plant

the size, timing and uptake rates of development

amount of recycled water available relative to the quantity users need

potential competing demands for recycled water.

Are there dual reticulation schemes operating in Australia?

Rouse Hill in Sydney’s north-west is Australia’s largest residential water recycling scheme, servicing more than

22,000 homes with around 1700 ML (1 ML = 1 million litres) of recycled water each year, reducing the demand for

drinking water from these households by about 40%. Eventually the scheme will serve around 36,000 homes.

Mawson Lakes, near Adelaide, operates a dual reticulation scheme which has halved the use of potable water, with

estimated savings of around 800 ML of water per year. Recycled water is also supplied to homes with a “third pipe”

in the Pimpama-Coomera area on the Gold Coast, the Magenta Shores development on the NSW Central Coast and

Newington/Sydney Olympic Park in Sydney.

Recycled Water

Dual Reticulation

INFORMATION SHEET 4.1

Dual reticulation pipework

Page 24: LHWP Information Sheets

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

The successful uptake of recycled water projects requires support

from the community

It can be hard to find suitable pipe routes in existing built-up urban

areas therefore the most practical case studies usually involve new

developments

Environmental considerations

Reduces drinking water demand by substituting drinking water

with recycled water for some household uses, such as flushing

toilets

Potential to support healthier waterways and marine

environments through reduced discharge of treated effluent

High energy use and greenhouse gas emissions unless offset by

renewable energy

Potential environmental impacts during construction

Social considerations

Non-weather dependent source ensuring a reliable water supply

A consistent supply for irrigation could improve the look and

usability of parks, playing fields and other open spaces without

using drinking water

Potential health risks if recycled water is not used as intended or

from cross-connection with drinking water plumbing

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 25: LHWP Information Sheets

What is greywater?

Greywater is the wastewater generated from washing machines, showers, baths and basins. When used safely,

greywater can replace drinking water for watering lawns and gardens. Water from the kitchen can also be reused as

greywater if the correct treatment process is put in place.

Greywater does not include water from toilets or urinals - this is sometimes referred to as blackwater.

How can greywater be used?

There are three ways that greywater can be reused:

manual bucketing - small quantities of water are collected from either the washing machine or the shower in a

bucket for reuse outside on gardens or lawns

greywater diversion devices - involves installing a diversion device to redirect greywater to the garden or lawn

via an irrigation system below the ground. A licensed plumber is required to install these devices. Local council

approval is not required as long as the conditions under Section 75A of the Local Government (General)

Regulation 2005 are met

greywater treatment systems - enables treated greywater to be used for flushing toilets, in washing machines,

and on gardens and lawns. Local council approval is necessary and the system must be installed by a licensed

plumber.

More information on greywater reuse and links to guidelines for households and more detailed factsheets are

available at www.waterforlife.nsw.gov.au/recycling/greywater.

What investigations into greywater reuse have been undertaken for the lower Hunter?

Some case studies for developing the Lower Hunter Water Plan have investigated greywater treatment systems to

service single lot households, as well as 10-dwelling housing and unit clusters in new developments.

Recycled Water

Greywater Reuse

INFORMATION SHEET 4.2

Diagram showing a typical cluster

scale greywater reuse system

Page 26: LHWP Information Sheets

Are there greywater reuse schemes operating in Australia?

Recycling schemes that collect and treat greywater for reuse are operating around Australia, including at Clovelly

House in Sydney, the Youth Hostel Association in Katoomba, the K2 Sustainable Housing Project in Melbourne and a

389 lot community at Bridgewater Lifestyle Village in Erskine, Mandurah WA.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

From low to medium, depending on form of reuse

Implementation considerations

The user is generally responsible for capital and operating costs

Ongoing maintenance is required to ensure consistent water quality

Environmental considerations Reduces drinking water demand by substituting drinking water with

recycled water for some household uses

Potential for high nutrient and salt concentrations affecting irrigation

use

Potential for run-off from irrigated grounds promoting algal growth in

waterways

Social considerations

Active community involvement in water management

Can require household behavioural changes and maintenance regime

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

Page 27: LHWP Information Sheets

What is decentralised water recycling?

Decentralised water recycling systems involve collecting and treating wastewater so it can be reused at or near the

point where the wastewater was generated. For example, a small housing development could have its own

wastewater treatment facility which treats and then recycles the wastewater for garden watering and toilet flushing.

Greywater reuse (discussed in Information Sheet 4.2) can also be considered to be a form of decentralised recycling.

Since all the infrastructure needed for decentralised schemes has to be newly built, these schemes are more suitable

for new developments rather than retrofitting into existing residential areas.

What is sewer mining?

Sewer mining is the process of tapping

into a wastewater system (generally

before it reaches the wastewater

treatment plant) and extracting raw

sewage, which is then treated and used

as recycled water.

The sewage is treated in a small onsite

facility to produce high quality recycled

water for use nearby. Sewer mining

plants may involve a combination of

filtration, biological, membrane and

disinfection processes. Waste from the

treatment process is generally returned

into the sewerage system.

Sewer mining projects can provide

recycled water for new or existing

developments. Recycled water

produced from a sewer mining

operation is commonly used to irrigate

sports fields, parks and golf courses. It

can also be used in some commercial buildings and industrial sites.

Are sewer mining and decentralised recycling being considered in the Hunter?

Investigations are being undertaken to determine opportunities where:

recycled water from sewer mining could be used to irrigate golf courses and sporting fields

decentralised recycling could service residential developments for uses other than drinking water, such as

toilet flushing, laundry washing, and garden watering.

Recycled Water

Decentralised Recycling and Sewer Mining Schemes

INFORMATION SHEET 4.3

Page 28: LHWP Information Sheets

Some potential industrial use schemes are also being investigated where recycled water could be used for cooling

towers, dust suppression and other operational processes.

Is sewer mining operating elsewhere in Australia?

Sewer mining projects to irrigate parks and sports fields are currently operating in Sydney at Mascot Airport, Olympic

Park, Pennant Hills Golf Course, Beverley Park Golf Course and Kogarah City Council. Southwell Park in Canberra,

Rocks Riverside Park in Brisbane, and the Council House 2 Office Building in Melbourne also use treated wastewater

for irrigation and other non-drinking uses.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Could be delivered by different organisations e.g. councils, developers or

private industry

The successful uptake of recycled water projects requires support from

the community

High upfront capital investment is usually required, often by the

customer or group developing the scheme, although some industrial and

irrigation schemes require less investment

Approval and consultation processes can be lengthy

Construction may disturb existing infrastructure in suburban areas

Environmental considerations

Potential to support healthier waterways and marine environments

through reduced discharge of treated effluent

High energy and greenhouse gases, unless offset by renewable energy

Potential environmental impacts during construction

Social considerations

Non-weather dependent source ensuring a reliable water supply

Demonstrates that improving water security is a shared responsibility

A consistent supply for irrigation could improve the look and usability of

parks, playing fields and other open spaces without using drinking water

Potential health risks if recycled water is not used as intended, from

unintended cross-connection with the drinking water supply, or if the

system is not properly maintained

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 29: LHWP Information Sheets

Can recycled water be used by industry?

Recycled water is suitable for industrial uses including dust suppression, generating steam, cooling tower water,

wash down and other operations. Using recycled water for industry can reduce the demand on drinking water

supplies as well as make use of treated wastewater. The recycled water usage level is also relatively constant, which

means the drinking water savings can be predicted more accurately.

Some of the benefits of using recycled water for industry include:

a number of users may be located close together so infrastructure can be shared

the level of additional treatment can be tailored to meet the end use (for example, steam generation needs

a higher quality than dust suppression)

the health risks are generally low for industrial uses.

Is industrial water recycling happening in the lower Hunter?

In 2011-12, Hunter Water supplied about 1,400 ML (1 ML = 1

million litres) of recycled water to industrial customers to use

as a substitute for drinking water. The largest industrial users

are currently Eraring Power Station and a coal washery. The

demand for recycled water can vary with rainfall and changes

in user needs, but industrial use often has a more constant

demand than other recycled water uses.

Eraring Power Station recycles water from the Dora Creek Wastewater Treatment Works for use in its high pressure

boilers, saving nearly 4 ML of drinking water every day. The recycled water is treated by microfiltration and reverse

osmosis to remove suspended solids, bacteria, viruses and dissolved salts because very high quality water is required

for the boilers. When this scheme started in 1994, Eraring Power Station was the first plant in the world to reclaim

water from sewage and use it as feedwater to high pressure boilers.

The Kooragang Industrial Water Scheme will provide 9 ML per day of high quality recycled water to industrial users

on Kooragang Island making it the largest recycled water project in the lower Hunter. The project is on track for

completion by December 2014.

The Kooragang scheme involves diverting treated effluent from the existing pipeline from Shortland Wastewater

Treatment Works to a new advanced water treatment plant located at Steel River. This plant will use membrane

microfiltration and reverse osmosis to produce high quality recycled water that will be pumped to industrial

customers on Kooragang Island via a new 8 km pipeline.

Are there more opportunities in the Hunter?

To support development of the Lower Hunter Water Plan, investigations are underway to identify other

opportunities to supply recycled water to large industrial users in the lower Hunter.

For example, some industrial customers on Kooragang Island may wish to expand their business and need more

water, while other large industries may choose to move to this area. Preliminary findings suggest the current

Recycled Water

Industrial Use of Recycled Water

INFORMATION SHEET 4.4

Eraring Power Station near Lake Macquarie

Page 30: LHWP Information Sheets

demand for recycled water on Kooragang Island is at least 9 ML per day, with potential for an additional 3 to 5 ML

per day by 2018. This may increase as new industries establish in future.

Opportunities are also being investigated to ensure enough recycled water can be made available in the right place

to meet future demands, which may involve diverting effluent from other treatment plants.

Is water recycling for industry occurring in other parts of the State?

One of Australia’s largest industrial water recycling schemes operates in Wollongong at BlueScope Steel, with up to

20 ML of recycled water being used each day. The nearby Port Kembla Coal Terminal also uses 1.25 ML of recycled

water each day for dust suppression, wash down and road cleaning operations. Rosehill Recycled Water Scheme in

Sydney supplies more than 8 ML of recycled water each day to five major industrial customers and a racecourse in

the Rosehill and Smithfield areas.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Uncertain timeframes for industrial growth and customer uptake of

recycled water

Risk of unused infrastructure if major industrial customers close

It can be hard to find suitable pipeline routes in existing built-up

urban areas

Some industrial customers might need assurance drinking water

will be available when the supply of recycled water is interrupted

(e.g. due to operational issues or maintenance down times)

Environmental considerations

Potential to support healthier waterways and marine

environments through reduced discharge of treated effluent

Energy is required for treatment and pumping (this may be able to

be offset with renewable energy)

Environmental impacts from construction and operation of the

water treatment plant (e.g. managing waste by-products)

Social considerations

Encourages investment in innovation and alternative water

efficiency and recycling technology

Demonstrates that saving water is a shared responsibility between

Hunter Water and industry

Some construction impacts on local community

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 31: LHWP Information Sheets

Water sources can be divided into surface water, such as in lakes, rivers and dams, and groundwater, which is stored

underground.

In the lower Hunter, surface water sources make a

major contribution to the region’s water supply

system. The amount of water supplied to Hunter

Water customers from Chichester Dam and

Grahamstown Dam varies from year to year. It can

range from 65-75% to over 95%.

Since the latest supply-demand balance indicates a

major new water source is not required at this time,

the Lower Hunter Water Plan will not consider new

surface water options. Opportunities to access water

from existing dams in adjoining regions (called inter-

regional transfers) are being investigated.

The options described in this series of information sheets include transferring water from:

the existing Lostock Dam, with potential options to enlarge the dam – this option would require agreement

from the owner, State Water

the Central Coast, involving ‘water banking’ in Mangrove Creek Dam and potential enlargement of the dam –

this would require agreement from Gosford City Council, Wyong Shire Council and the Central Coast Water

Corporation.

Environmental flows from dams

Dams and weirs affect the natural flow of water in rivers and streams. To help lessen these impacts, some water is

released from the storages back into the river downstream of the dam. These releases are called environmental

flows. They help restore the ecology and biodiversity of water dependent ecosystems. Fishways are also built at

dams and weirs to allow fish to move up and down stream.

Chichester Dam and Seaham Weir (on the Williams River) are licensed by the NSW Office of Water. The water

licences include conditions called ‘environmental flow rules’ that aim to help protect aquatic health by providing a

share of water for the downstream environment. Changes to environmental flow rules for Chichester Dam and new

conditions for Seaham Weir are being investigated

which aim to achieve more variability in flows to reflect

natural conditions. These investigations are running in

parallel with the development of the Lower Hunter

Water Plan.

Surface Water

Surface Water - Overview

INFORMATION SHEET 5.0

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

Grahamstown Dam

Page 32: LHWP Information Sheets

What would an inter-regional transfer related to Lostock Dam involve?

Lostock Dam is located on the Paterson River approximately 93 km

north-west of Newcastle. The dam, constructed in 1971, has a storage

capacity of 20 GL (1 GL = 1 billion litres) and is managed by State

Water. It supplies water to licensed users on the ‘regulated’ section of

the Paterson River, which is from the dam to the tidal limit as shown in

the map at right.

While the dam was built to supply downstream agriculture, the volume

of water available is not used to its full capacity.

Options using Lostock Dam to improve water security for the lower

Hunter region are being investigated for both the short and the longer

term.

The short term option involves purchasing existing water licences on

the Paterson River. Licences purchased on the water transfer market

could provide Hunter Water with access to additional water for use as

part of a drought response. The water would need to be treated and

transferred into Hunter Water’s existing water supply network.

A longer term option could involve enlarging the existing dam, with

preliminary investigations having considered three storage capacity

options between 33 GL and 67 GL.

Preliminary engineering feasibility studies

indicate that a 65% increase in dam

capacity, from 20 GL to 33 GL, could be

achieved by installing gates along the

existing spillway crest, along with some

minor works along the embankment crest.

Options for further enlargements would

involve raising the dam embankment and

building a new spillway. The raised

embankment would be of similar

construction to the existing embankment.

Under both the short term and long term

scenarios, water would be released from

the dam and extracted at a location

further downstream. If the water was

transferred to Grahamstown Dam it could

Surface Water

Inter-regional Transfers: Lostock Dam

INFORMATION SHEET 5.1

Lostock Dam

Page 33: LHWP Information Sheets

be treated through the existing water treatment plant. Alternatively, a local water treatment plant could be built

with water pumped into the water supply network near Maitland.

Arrangements for environmental flows releases would be determined based on detailed environmental

investigations and the regulatory requirements set by relevant government agencies.

The Water Sharing Plan for the Paterson Regulated River was gazetted on 1 July 2007 and applies for a period of 10

years. This plan specifies how water is shared between water users and the environment.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Dam enlargement options could increase the water supplied, cost and lead time

to a rating of ‘high’

Implementation considerations

Preliminary engineering feasibility studies have found that the existing

dam embankment should be suitable to incorporate the potential dam

raising options.

Detailed investigations on the existing embankment and foundations,

and environmental investigations would be required.

Purchase of water licences depends on availability on the water

transfer market.

Environmental considerations

Makes use of existing infrastructure

Inundation of nearby land (if dam were enlarged)

Potential impacts on the aquatic environment from altered flow

regimes

Any new infrastructure may have associated environmental impacts

Increased water pumping requires additional energy and emits

greenhouse gases unless offset by renewable energy

Social Considerations

Would increase community and business confidence in regional water

supply security

Construction impacts on the local community

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 34: LHWP Information Sheets

What would an inter-regional transfer with the Central Coast involve?

The lower Hunter and Central Coast water supply systems are connected via a pipeline linking reservoirs located at

Kanwal and Morisset. The existing link can transfer up to 33 ML per day (1 ML = 1 million litres) to the Central Coast

system. Due to operational and capacity limitations of the infrastructure, the return transfer rate to the Hunter

system is currently an average of 13 ML per day.

The pipeline link between the two regions was used to supply water from the lower Hunter to the Central Coast

when their storages reached very low levels during the last drought. The price for transferred water was determined

by the Independent Pricing and Regulatory Tribunal (IPART).

The Central Coast’s water supplies are now more secure with construction of the ‘Mardi-Mangrove Link’ - comprising

a 21 km pipeline linking Mardi and Mangrove Creek Dams, together with two new pumping stations. This allows

additional water to be pumped from the Wyong River and Ourimbah Creek during wet periods and transferred to

Mangrove Creek Dam.

In conjunction with Wyong Shire Council, Gosford City Council and the Central Coast Water Corporation,

investigations have begun into the feasibility of supplying water from the lower Hunter network to the Central Coast

network during normal conditions, and ‘banking’ an equivalent amount of water in Mangrove Creek Dam. The water

could then be returned (‘withdrawn from the bank’) when storages in the lower Hunter are low.

A water banking arrangement would aim to optimise regional water storages and provide greater water security to

both regions, particularly during drought.

Surface Water

Inter-regional Transfers: Central Coast

INFORMATION SHEET 5.2

Map showing the link

between the lower Hunter

and Central Coast water

supply networks.

It also shows the Mardi-

Mangrove link.

Page 35: LHWP Information Sheets

Mangrove Creek Dam is located on Mangrove

Creek, a tributary of the Hawkesbury River,

approximately 50 km north-west of Gosford.

The dam was built in 1981 and has a storage

capacity of 190 GL (1 GL = 1 billion litres).

When the dam was built, allowance was

made for future enlargement.

Investigations are underway - in consultation with Gosford City Council, Wyong Shire Council and the Central Coast

Water Corporation - to consider options to enlarge Mangrove Creek Dam to provide additional storage capacity for

‘banking’ of water. Storage capacity options up to around 270 GL will be investigated. The feasibility of increasing the

transfer capacity of the lower Hunter and Central Coast water supply networks will also be investigated.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

Water

UNDER INVESTIGATION

Cost

UNDER INVESTIGATION

Lead time

UNDER INVESTIGATION

Implementation considerations

If investigations indicate this option is feasible, agreement would need

to be reached between the water supply authorities regarding the

conditions for water transfers and banking, and financial

considerations.

Environmental considerations

Makes use of some existing infrastructure

Inundation of nearby land (if the dam was enlarged)

Increased water pumping requires additional energy and emits

greenhouse gases unless offset by renewable energy

Any new infrastructure may have associated environmental impacts

Social considerations

Would increase community and business confidence in regional water

supply security

Interconnectivity of the network increases system flexibility and

security for the lower Hunter and Central Coast

Construction impacts on the local community

Both the lower Hunter and Central Coast communities may be

concerned about how water and costs would be shared fairly

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Mangrove Creek Dam

Page 36: LHWP Information Sheets

Water sources can be broadly classified as either surface water, such as lakes, rivers and dams, or groundwater,

which is stored underground.

Groundwater can be found at various depths from at or near the surface, to hundreds of metres below ground. It is

stored in sands, soils, and in cracks and crevices between rocks. Groundwater can be accessed using spear points or

bores and used for town water supplies or irrigation.

In the lower Hunter, groundwater sources are an important part of the region’s water supply system. The amount of

water supplied to Hunter Water customers from groundwater at Tomago and Tomaree varies from year to year. It

can range from less than 5% up to 30-35%.

In developing the Lower Hunter Water Plan, new groundwater sources that could contribute to the region’s future

water supply needs are being investigated in consultation with key stakeholders including the NSW Office of Water.

The groundwater options currently being considered are described in this series of fact sheets and include accessing:

deeper water stored in the Tomago aquifer (as a potential emergency measure)

other groundwater sources in the lower Hunter, such as the ’Hunter Alluvial’ source near the junction of the

Hunter and Paterson Rivers

groundwater that collects in mines.

Groundwater

Groundwater - Overview

INFORMATION SHEET 6.0

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

An existing bore used to pump water from the Tomago Sandbeds

Page 37: LHWP Information Sheets

Can more water be sourced from the Tomago Sandbeds?

The Tomago Sandbeds extend approximately 25 km

north-east from Tomago to Lemon Tree Passage,

and lie parallel to the coast between Newcastle and

Port Stephens, as shown in the map.

The amount of drinking water provided to Hunter

Water customers that is sourced from the Tomago

Sandbeds can vary from year to year, up to a

maximum of around 20-25%.

This aquifer can store approximately 100,000 ML

(1 ML = 1 million litres) of water above sea level.

It is refilled from rain that falls directly on the sand surface.

At present, a network of bores and

vacuum stations operated by Hunter

Water can access approximately

60,000 ML of ‘active storage’, as shown

in the figure below.

The amount of water that Hunter

Water can extract from the sandbeds is

licensed by the NSW Office of Water.

Hunter Water must stop pumping

when the water drops to a set level.

This is important to minimise impacts

on the ecosystems that depend on

groundwater and so that a reliable,

good quality supply is maintained.

Hunter Water has estimated there is a

further 40,000 ML of groundwater

below the current level where pumping

must stop, and has investigated the

potential to extract up to 25,000 ML of

this groundwater.

The NSW Office of Water would only permit access to this ‘deep Tomago’ water if Hunter Water can demonstrate,

through scientific studies, that there would not be any adverse impacts on the environment. Investigations have

begun but results are unlikely to be available before the Lower Hunter Water Plan is developed.

Groundwater

Deep Tomago Groundwater

INFORMATION SHEET 6.1

Map showing the location of the Tomago Sandbeds

Schematic cross-section of the Tomago Sandbeds

Page 38: LHWP Information Sheets

If approved as an emergency drought response, the water available from the deep storage would only be available

for a limited period – estimated at around 18 months if water was pumped at 45 ML per day. After this time,

pumping would have to stop until the groundwater was naturally refilled by rainfall.

If permitted, the deep storage could be accessed by converting existing pumping stations, building new bores or re-

establishing bores that are no longer in use, and upgrading the power supply. Water accessed from lower depths

may have high levels of manganese, iron and other metals, so the water may need additional treatment before being

treated at the existing Grahamstown water treatment plant.

Fresh groundwater in the sandbeds sits above sea level. Another important issue with this option, is to ensure

pumping stops before reaching the level where there would be a risk of salt water entering the fresh groundwater

resource and making it unsuitable for future use. The potential for sea level rise due to climate change would also

need to be considered.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementation considerations

Access to the deep storage is not permitted under the existing water

licence

The regulatory requirements may be reconsidered in a drought

emergency

Environmental considerations

May adversely impact on ecosystems that depend on groundwater

(Tomago Sandbeds are located in the Tilligerry State Conservation

Area)

Pumping must be carefully controlled to avoid the potential for

saltwater intrusion into the freshwater aquifer

Social considerations May be an emergency option to extend water supplies in a severe

drought

Minimal disruption to the community as works would be

undertaken on land that is closed to the public

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 39: LHWP Information Sheets

Are other groundwater sources available?

Groundwater sources are already an important part of the lower Hunter’s water supply, with significant

groundwater sources at Tomago and Tomaree.

To support development of the Lower Hunter Water Plan, the potential for other groundwater sources in the lower

Hunter (or nearby) has been investigated. One potential source is known as the ’Hunter Alluvial’ source, which refers

to groundwater near the junction of the Hunter and Paterson Rivers in the Morpeth – Bolwarra area.

Initial investigations will test the water quality and explore the size, depth and location of the groundwater source.

These studies are the first steps in assessing the feasibility of this as a potential additional source for the lower

Hunter which might be accessed in a drought. These investigations are planned for mid 2013.

If investigations indicate this may be a feasible source of water, this option would most likely involve installing a

number of extraction bores, pumps and a pipeline delivering water to a temporary treatment plant and into the local

water supply network.

Groundwater

Hunter Alluvial Groundwater Source

INFORMATION SHEET 6.2

Schematic cross-section of Hunter alluvial showing potential aquifers at different depths

Page 40: LHWP Information Sheets

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

Water

UNDER INVESTIGATION

Cost

UNDER INVESTIGATION

Lead time

UNDER INVESTIGATION

Implementation considerations

Further information is needed on the quality and quantity of

groundwater to assess the feasibility of this potential option

This groundwater source is not part of an existing Water Sharing

Plan, and there is limited information on any existing users

Environmental considerations

Extraction from deep aquifers is likely to have less environmental

impact compared with shallow aquifers because there would be

less chance of disturbing acid sulfate soils or impacting on wetlands

Construction impacts are anticipated to be minor as infrastructure

would be located in previously disturbed locations

Deep aquifers may have low recharge rates and other users may be

impacted due to slow replenishment

Social considerations

Water would need to be shared with existing stock, domestic and

irrigation users in the area

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 41: LHWP Information Sheets

How can mine water help the region’s water supply?

The Hunter region has a long history of coal mining, with many underground and open cut mines. As part of the

mining process, voids are formed, which can fill with water.

Some of the mine workings are below the water table, and water has to be removed to allow safe operation of the

mine. The water may come from groundwater or from rainfall or runoff that collects in the mine.

Mine water is generally used by the mine for operational needs such as dust suppression, drilling, or coal washing.

Some mines in the lower Hunter have more water than they need. The quality of the mine water – including salt,

acidity and mineral content – would influence the treatment needed before it could be used, recycled or discharged

to the environment under a licence from the Environment Protection Authority.

Investigations into the potential to use groundwater from mines as a water supply option for the Lower Hunter

Water Plan are at a very early stage. More information is needed regarding the quantity and quality of groundwater

available from operating or abandoned mines to determine if this is a feasible option for the region.

It is important to note that any water used for drinking water supplies must meet the Australian Drinking Water

Guidelines.

Is mine water used in Australia for consumption?

In 2006, investigations for the Metropolitan Water Plan studied the potential sources of groundwater from mines

near Sydney as potential emergency drought supplies. Abandoned mines that were flooded with water as well as

operating mines were investigated.

A recent report prepared for the National Water Commission states that ‘…there are several cases where excess

mine water has been, or is proposed to be, made available to supply towns, agriculture or industry independent of

the mine… One example is Clarence Colliery near Lithgow, NSW, where part of the mine’s excess incidental water is

supplied to Lithgow for town water, and part is treated and discharged into a river.’

(Source: Integrating the mining sector into water planning and entitlements regimes, NWC, Waterlines Report Series No 77, March 2012)

Groundwater

Mine Water

INFORMATION SHEET 6.3

Page 42: LHWP Information Sheets

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

Water

UNDER INVESTIGATION

Cost

UNDER INVESTIGATION

Lead time

UNDER INVESTIGATION

Implementation considerations

If water was drawn from a working mine, the ongoing availability of

water if the mine was sold or shut down would need to be

addressed

If mine water was found to be a feasible option, a pilot plant might

help to demonstrate safety and reliability

Geological stability may be an issue for the concept of using

abandoned mine workings to store water

Environmental considerations

Surplus mine water could be treated and used as a resource instead

of discharged to the environment

Construction impacts may be minimal if infrastructure is located in

previously disturbed locations

Mine water might contribute to streamflow, either directly or

through groundwater

Social considerations

Potential community concerns about water quality

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 43: LHWP Information Sheets

What is desalination?

Desalination is the removal of salt and other minerals from saline water (such as seawater) to produce fresh water

for drinking water supply or industrial uses needing high quality water.

Thermal desalination is achieved by boiling the salt water and condensing the steam to produce fresh water (ie, a

distillation process). Reverse osmosis uses semi-permeable membranes and pressure to separate salts from water.

The salt water is moved across membranes that block salts and other particles so that only water can pass through.

A by-product is a concentrated salt solution called brine that needs to be disposed of. Reverse osmosis generally

requires less energy than thermal desalination. The reverse osmosis process is represented in the diagram below.

Desalination provides a source of drinking water that does not rely on rain. It does require a significant amount of

energy to operate, although renewable energy can be used to offset this in some cases. Desalination options being

investigated for the lower Hunter include:

small scale temporary units to supplement water supplies during a drought

“readiness” activities for a larger scale permanent desalination plant for emergency development in a

drought.

Desalination

Desalination - Overview

INFORMATION SHEET 7.0

Desalination by

reverse osmosis

Schematic showing reverse

osmosis process

Page 44: LHWP Information Sheets

What is temporary desalination?

Temporary desalination can be used to supplement water supplies on a small scale during an extended drought. The

facilities can be located on land or sea and can be constructed using modular container systems.

The capacities of portable plants vary. Individual land-based, container style plants of 1 - 3 ML per day (1 ML = 1

million litres) are available and have been used in the Hunter for wastewater and mine water applications. A

number of these modular containers can be connected together to provide increased total production capacities.

For example, a portable modular unit providing 20 ML per day has been used in Limassol, Cyprus (pictured below).

Ship based plants are either specially built or converted tankers or barges. Existing barges in Saudi Arabia have

reported capacities of 25 ML per day. Companies in Israel and America are marketing ship platforms with capacities

of 50 - 100 ML per day.

Temporary desalination plants require additional infrastructure. For land-based plants, this would include raw

saltwater intakes from the ocean or estuary (which are different to intakes for permanent desalination e.g. through

open water pipes or buried sand dunes inlets), outlets for brine discharge, connection pipes to the water distribution

system, and possibly power upgrades. Ship-based systems are typically self-contained with on-board generators and

an inlet and outlet for brine disposal. They would require a connection pipe to the water distribution system and a

safe mooring point.

As the portable facilities are relatively small, they could be added to the water supply network at multiple coastal

locations across the lower Hunter on a temporary basis during a drought. However, they could only produce enough

water to meet a small fraction of the region’s water supply needs.

The plants could be located in open space areas such as parklands and car parks adjoining coastal and estuarine

areas, where they would connect to the local water network. The plants would be temporary and would be removed

when no longer needed, although some infrastructure such as pipelines may remain.

Are there any temporary desalination plants in Australia?

Small modular desalination units have been

used widely across Australia for industrial

purposes, for example in mining and

wastewater applications. During the most

recent drought, the Central Coast investigated

the installation of several portable units,

however they were not required as drought

conditions ceased.

Ship based plants have not been used in

Australia but were investigated by other

water utilities during the recent drought.

Desalination

Temporary Desalination Facilities

INFORMATION SHEET 7.1

A modular desalination plant

Page 45: LHWP Information Sheets

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

A long drought and/or larger number of portable desalination units could

increase the water supplied to a rating of ‘medium’

Implementation considerations

Physical capacity limitations in the distribution system will restrict

the population the plants could service

The site must have access to salt water, sufficient power supply,

and access to the water supply distribution system

Intake water quality issues, particularly in lakes and estuaries

where flushing during drought periods may be poor

Constructing pipes in urbanised areas may be difficult with risk of

slow construction timelines

Any temporary, above ground pipelines would have a risk of

accidental damage or vandalism

Pollution discharge licences would be required for brine disposal

Environmental considerations

Potential environmental impacts would be temporary rather than

ongoing

Potential for brine release to impact on the aquatic environment

Potential environmental impacts from plant construction

Plant operation requires energy and emits greenhouse gases

unless offset by renewable energy

Liquid wastewater from pre-treatment processes

Storage of hazardous chemicals

Social Considerations

Non-weather dependant source

Potential social impacts would be temporary rather than ongoing

Visual amenity impacts, depending on site

Potential high disruption impacts as plants are noisy and may

require 24 hour operation

There may be road and access disruptions as a result of

construction and pipework installation

Disruption to beaches or loss of access to open spaces, depending

on location of site(s) and temporary pipelines

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go to

haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.

Page 46: LHWP Information Sheets

What does a permanent desalination facility involve?

A desalination plant can be designed to operate continuously to supply drinking water (known as a “base load”

plant). This is one way to diversify a region’s water supply sources so the system is less vulnerable to drought. The

plan is not considering this option.

However, a permanent emergency plant designed to provide water during a drought could be built in stages as the

drought progresses, which means a smaller plant would be in place if drought conditions ended.

A potential modular approach with construction in stages could consist of three units, each supplying 40ML per day.

This could provide the following benefits during drought:

One module (40 ML per day) could slow down the rate of decline of the existing water storages

Two modules (totalling 80 ML per day) could work in combination with other water sources to provide

enough water to meet all essential water needs, assuming demand was reduced by restrictions and water

efficiency

Three modules (120 ML per day) could provide enough water to meet essential (very restricted) needs

without requiring water from any additional sources. In the case of drought, where all other storages were

depleted, this would provide a secure source of water that does not rely on rain.

How could we plan ahead with ‘readiness activities’?

Building an emergency desalination plant typically needs a lead time of more than five years to allow for site

selection, environmental and other investigations, planning approvals, design and construction. To reduce this lead

time, a series of ‘readiness activities’ could be completed to speed up construction should there be a severe drought.

‘Readiness activities’ would include actions such as selecting a suitable site, undertaking detailed environmental and

engineering studies, and obtaining planning approval. These activities could be completed in the short-term and

would mean that the commitment to construction would not need to be triggered until later in a drought.

A permanent facility in the lower Hunter would have to be located close to the coast to access seawater. Further

environmental and engineering investigations would be needed to select a suitable site, probably between Belmont

in the south, and Williamtown in the north. Access to sufficient power supplies is also a key consideration.

Another option to consider is whether there are potential opportunities for a desalination plant that could serve

more than one region.

The ‘readiness’ approach was put in place on the

Central Coast during the last drought, with planning

approval for a desalination plant at Toukley that

could produce 20 ML per day. The plant will not be

built unless required due to a severe drought.

Desalination

Emergency Desalination Facility

INFORMATION SHEET 7.2

Reverse osmosis technology extracts salt from seawater

Page 47: LHWP Information Sheets

Are there permanent desalination facilities in Australia?

Desalination was one of the major initiatives of the 2006 Metropolitan Water Plan for Sydney. Construction of the

plant at Kurnell was triggered in early 2007 during the deepening drought when dam levels were nearing 30% . The

lead time for building the plant was considerably reduced by having completed a series of ‘readiness activities’.

Sydney’s desalination plant can provide up to 15% of Sydney’s water needs, or 90 billion litres a year. The seawater

is sourced from the Tasman Sea. With dam levels recovered after the drought, the plant is currently shut down.

Desalination facilities are also in place or under construction in Perth, Adelaide, Melbourne and the Gold Coast.

There are over 3,500 land-based desalination plants around the world.

The table below gives a general indication of the amount of water supplied or saved, cost, lead times and

environmental and social considerations (positive or negative) for this option.

LOW MEDIUM HIGH

Water

Cost

Lead time

Implementing ‘readiness activities’ in the near term would reduce the lead time

in a drought

Implementation considerations

Desalination would provide flexibility for drought conditions by

diversifying the region’s water sources.

Significant cost for ‘readiness activities’ to reduce potential lead time

for construction, rather like investing in insurance.

The site must have access to salt water, sufficient power supply, and

access to the water supply distribution system

Pollution discharge licences would also be required for brine disposal

Environmental considerations

Potential for brine release to impact on the aquatic environment

Plant operation requires energy and emits greenhouse gases unless

offset by renewable energy

Major infrastructure project with construction disturbance in the

immediate plant site and supporting infrastructure such as roads,

power and pipelines (generally underground)

Social considerations

Would increase community and business confidence in regional

water supply security

Employment opportunities to construct and operate the plant

Construction impacts on local community

Visual amenity impacts, depending on site

Lower Hunter Water Plan Project Team

PO Box 2297

DANGAR NSW 2309

PH 1800 503 866 FX 4908 4954

To have your say online or to register for a workshop, go

to haveyoursay.nsw.gov.au/lowerhunterwaterplan

This series of fact sheets is designed to summarise

information from investigations to April 2013.

The environmental and social considerations

are provided as examples only and are not

intended to be a comprehensive list.